2017
DOI: 10.1002/apj.2075
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Kaolinite induced control of particulate lead and cadmium emissions during fluidized bed waste incineration

Abstract: Kaolinite was utilized as in-furnace sorbent to control submicron lead (Pb) and cadmium (Cd) emissions during waste incineration in a fluidized bed furnace. The secondary combustion chamber temperature ranged from 850 to 1000°C. The metal capture was investigated for aspects of chemical reaction, physical conglutination and control performance of submicron metal emission. Pb reacted with kaolinite and caused conglutination of nanoscale metal particles at a lower temperature than Cd. Emission control of submicr… Show more

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Cited by 11 publications
(5 citation statements)
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“…The temperature of municipal solid waste (MSW) incineration is usually 800-1200 • C, at which, semi-volatile heavy metals and alkali metals exist mainly in the form of chloride vapor, such as PbCl 2 , PbCl, CdCl 2 , CdCl, NaCl and KCl [40][41][42][43]. In the condition of in-furnace injection, the residence time of kaolinite in the furnace is usually less than 2 s, so 15-55% of hydroxyl groups or more would remain in kaolinite.…”
Section: Effect Of Dehydroxylation and Structural Distortion On Metalmentioning
confidence: 99%
“…The temperature of municipal solid waste (MSW) incineration is usually 800-1200 • C, at which, semi-volatile heavy metals and alkali metals exist mainly in the form of chloride vapor, such as PbCl 2 , PbCl, CdCl 2 , CdCl, NaCl and KCl [40][41][42][43]. In the condition of in-furnace injection, the residence time of kaolinite in the furnace is usually less than 2 s, so 15-55% of hydroxyl groups or more would remain in kaolinite.…”
Section: Effect Of Dehydroxylation and Structural Distortion On Metalmentioning
confidence: 99%
“…Besides, many other factors in the actual waste incineration also had a significant influence the heavy metal capture performance, the impact extents and influence mechanism of these factors were different. Using PbCl 2 and CdCl 2 as source of heavy metals, capture efficiency of Pb by kaolin in the thermogravimetric reactor was above 80 %, [4] while that of Cd was only about 10 %. [5] While Yao et al used the similar thermogravimetric reactor to obtain the capture efficiencies of PbCl 2 and CdCl 2 by raw kaolin both about 40 %-50 % at 800 °C.…”
Section: Introductionmentioning
confidence: 98%
“…Pb mainly exists in coal, municipal solid waste, industrial solid waste and other solid wastes or fuels. 1 , 2 During the heat treatment or combustion of these solid substances or fuels, a large amount of lead evaporates and is discharged into the atmosphere together with high-temperature flue gas. 3 , 4 When the smoke cools to a certain point, the lead vapor condenses and partially forms PM1 (lung-accessible particulate matter) and even smaller PM0.1.…”
Section: Introductionmentioning
confidence: 99%